article (pdf)

ORNIS SVECICA 15: 13–21, 2005
Wintering swans Cygnus spp. and Coot Fulica atra in the Öresund,
South Sweden, in relation to available food recources
Övervintrande svanar Cygnus spp och sothöns Fulica atra i Öresund, södra
Sverige, i relation till tillgängliga födoresurser
LEIF NILSSON
Abstract
In connection with the building of a Fixed Link (bridge –
artificial island – tunnel) between Sweden and Denmark
intensive studies of waterfowl and benthic fauna and flora
in the Öresund were undertaken as a part of the Environmental Impact Assessment Study. This paper analysis
the occurrences of staging and wintering herbivores (i.e.
Mute Swan Cygnus olor and Coot Fulica atra) in relation to available food resources. It was concluded that the
proportion of Zostera and Ruppia consumed by the birds
during September–March was about 10% of the available
standing crop in the autumn or less. During ice-periods
large parts of the available feeding areas are covered by
ice, and during an extended ice-period in 1995/1996 the
calculated food consumption for the ice-free areas was
of the same magnitude as the calculated standing crop
of food plants.
Leif Nilsson, Department of Ecology, Lund University,
Ecology Building, S-223 62 Lund, Sweden. E-mail: leif.
nilsson@zooekol.lu.se
Received 9 August 2004, Accepted 27 November 2004, Editor: Å. Lindström
Introduction
The southern part of the Öresund between Sweden
and Denmark has long been known as an internationally important staging and wintering area for
a number of different waterfowl species (Nilsson
1975, 1996a). Part of the area (Falsterbo–Foteviken) is listed among the Swedish Ramsaar-sites, as
is the case for the Danish island of Saltholm. Moreover, a number of other sites in the Öresund do also
full-fill the criteria for internationally important
wintering sites for waterfowl, even if they have not
been designated as internationally important areas
under the Ramsaar-convention.
Due to the importance of the area for a number
of bird species, intensive studies of staging and
wintering waterfowl on both the Swedish and Danish side of the Öresund were included in the Environmental Impact Assessment (EIA) study for the
Fixed Link between Sweden and Denmark which
was build during the latter part of the 1990s and
which was ready in the summer of 2000 (Öresundskonsortiet 1995, 1998). This link, which is 16 km
long, consists of a combined railroad and motorway
connection from Lernacken on the Swedish side of
the Öresund to Kastrup in Denmark, including a
1092 m long high bridge, 6700 m of connecting
bridges, an artificial island and a 3500 m sink-tunnel.
One of the conditions for building the fixed link
was that the construction should not obstruct the
water currents in and out of the Baltic Sea, which
are of vital importance for this sea area. Thus largescale compensatory dredgings were undertaken in
addition to the dredging for the construction of the
bridge and tunnel. As there was a potential risk that
excessive sediment spill from the dredging could
have a negative effect on marine life in the area,
including staging and wintering waterfowl, an extensive monitoring programme on the benthic flora
and fauna as well as waterfowl was included in a
Control Programme. Thus data on the availability
of important food species for swans and Coot were
collected and could be used for comparison with
waterfowl census data from the same areas.
In this paper I will relate the occurrence of waterfowl feeding on aquatic vegetation (i.e. swans
and Coot) in the study area during the non-breeding season to their food supply, whereas the occurrence of the different waterfowl species in the
southern part of the Öresund will be described
elsewhere (L. Nilsson & M. Green, in prep.). More
detailed data from the waterfowl work are found in
technical reports from the project, where the pos13
sible effects of the construction work on the bird
fauna have been evaluated in detail (see Nilsson
1996b, 1998, 1999a, 1999b, 2001. Regular waterfowl counts have been undertaken in the area since
1964/65 (Nilsson 1996a, unpubl.).
Study area
The general area for the impact assessment study
related to the Fixed Link was from Fasterbo in the
south to Barsebäck (Figure 1, cf. Nilsson 1996b,
1998), but more intensive studies were undertaken
closer to the construction site and to the south of
it. The possible impact zone according to the EIA
(Öresundskonsortiet 1995, 1998) extends to and
includes the Malmö harbour area, but the area
between Lernacken (where the bridge reaches the
Swedish coast) and Malmö has very little of natural waterfowl habitat, especially for herbivorous
birds.
Lernacken in the north of the study area is an
area of artificial hills in the shore-line created from
deposits of calciferous material. Further south
Klagshamn is an artificial peninsula made of similar material from excavations. Originally, the area
between Lernacken and Foteviken had grazed shore
meadows but north of Klagshamn the meadows are
no longer grazed as is also the case for some areas
south of Klagshamn. Anyhow, Foteviken still has
the largest area of grazed marine shore meadows
in Sweden.
The water area between Lernacken and Foteviken is in general very shallow, large parts having a
water depth of less than 3 m (Figure 1), extensive
areas having a depth of less than 1 m. The inner
parts are muddy with patches of Ruppia, whereas
extensive Zostera meadows on sand are found
further out (VKI/Toxicon 1996a, 1996b, 1996c,
SEMAC 1997, 1998).
Due to the currents in the Öresund the waters
off Lernacken are among the last areas to freeze
during hard winters, the area of open water sometimes extending south to the Klagshamn peninsula,
whereas the rest of the southern part of the Swedish
Öresund coast is totally ice-covered. Moreover, just
south of Lernacken the current keep even shallow
water free of ice during cold periods.
Material & Methods
Waterfowl counts
The utilization of the area by feeding waterfowl
was based on the calculation of bird-days for the
different species in different areas. In 1995/1996
14
Figure 1. Map of the study area in the Öresund. For a general
position in south Sweden, see inserted map. Areas with a water depth of less than 3 m marked with grey tone.
Karta över undersökningsområdet i södra Öresund. Områden med ett vattendjup om mindre än 3m markerade med grå
ton.
and 1996/1997 counts were undertaken each week
in the entire area between Barsebäck and Falsterbo
(Nilsson 1996b, 1998, Nilsson & Green in prep),
of which the present study area (Figure 1) forms
a part. Counts of all species were also performed
each week during August–March 1997/1998 in the
main study area (Nilsson 1999a).
The counts were undertaken from the shore either through telescopes from fixed observation
points so situated that the entire sectors could be
covered or by the observer walking along the shore
line. Telescopes with 20–50 X magnification were
regularly used. Counts were only undertaken during good weather conditions. For a thorough description and discussion of census methods see
Nilsson (1975, 1976, 1991).
Estimation of food consumption of different
species
Among the plant feeders, swans (mainly Mute
Swans Cygnus olor) and Coot Fulica atra are important in the study area. They regularly feed on
Ruppia and Zostera in the area. The consumption
of sea grasses by the moulting Mute Swans of Salt-
holm have been evaluated by Clausen et al. (1995,
1996), where a thorough discussion of the calculation of energy consumption of swans is found. There
was a marked variation in the different estimates of
the food consumption of swans, between 352 g and
620 g dry-weight of Zostera per 24 h. Mathiasson
(1973), who also studied moulting Mute Swans,
estimated the daily food consumption to 3.66 kg
wet weight, corresponding to 586 g dry weight.
Measurements and estimates from other parts of
the season are lacking. In the calculations here I
have used an overall value of 3.5 kg fresh weight as
the daily consumption, i.e. in the higher part of the
interval as the estimates were for summer time but
the present study relates to the entire year. Studies
of the Canada Goose Branta canadensis (Williams
& Kendeigh 1982) showed that the energy consumption of geese (and also other waterfowl) will
be about 25–30% higher in winter than in summer.
Thus a 25% higher estimate was used for the iceperiods in the winter, i. e. 4375 g fresh weight.
The Coot is normally considered a plant feeder
(Borowiec 1975, Hurter 1972, 1979) but can also
use animal food, e.g. Suter (1982) found it feeding on Dreissena in the Lake of Constance. It is
not known to which extent it utilises animal food
in the Öresund area. Based on laboratory studies
and field observations Hurter (1972, 1979) estimated the food requirements of the Coot for different
plant foods as follows: Bromus racemosus 640 KJ/
24 h (1110 g fresh weight), Phragmites communis
706 KJ/24 h (730 g), Potamogeton pectinatus 710
KJ/ 24 h (2980 g) and Ranunculus fluitans 1000
KJ/ 24 h (3650 g). Ruppia is apparently an important food for the Coot in brackish water (Verhoeven
1980). According to three different methods he
gives the consumption of Ruppia as 38.1, 52.3 and
82.8 g/24 h ash-free dry-weight but considers the
middle value as the most correct one. This corresponds to a daily food consumption of 305 g fresh/
weight, which will be used in the calculations here.
In line with the discussion above a 25% higher estimate was use for the ice-period, i.e. 375 g fresh
weight/24 hours.
ing on the shore meadows and farmland in the
autumn and winter, even if small flocks can feed
on floating Zostera. The Wigeon is not considered
any further here. The Whooper Swan has in recent
years to a large extent become a terrestrial feeder,
but still a proportion of the swans in the area feed
on submerged vegetation (the terrestrial Whoopers
not being included in the counts). Large numbers
of especially Canada Geese Branta canadensis use
the Foteviken area as their night-time roost. They
feed in the surrounding fields, but can occasionally
feed on Zostera. The geese are not considered any
further here.
The southern part of the Öresund is an important
area for Mute Swans all the year round. Important
numbers moult in the Öresund, especially on the
island of Saltholm, but there are also large flocks in
summer in the Foteviken area. During autumn there
is a steady built-up in numbers of swans in the area,
reaching peak numbers of between 2000 and 2500
in 1995/96 and between 1500 and 2000 in the other
two years shown in the graph (Figure 2). The highest peaks in especially 1995/96 were found during
the ice-period.
The Mute Swans occur all over the area, but
numbers in the Foteviken area are appreciably
higher than in the area between Lernacken and
Klagshamn during normal periods. In periods with
ice there is however a concentration of the Mute
Swans in the areas close to Lernacken as these are
the last to freeze in this part of Öresund.
The Whooper Swan is a regular winter visitor to
the area (Figure 2). Peak counts have been around
150. Generally there are more Whooper Swans in
the Foteviken area, but in recent years there has
been a change in their habits and more and more
swans are feeding in the fields.
The Coot is also a regular staging and wintering
bird in the area with flocks feeding both in Foteviken and north of Klagshamn. Peak counts in some
years were 2000 and more, occurring during the
autumn, whereas winter counts were lower.
Results
Using literature data for the food consumption (see
methods) and the number of bird-days from the
counts, it was calculated that the swans using the
area between Lernacken and Foteviken consumed
between 780 and 1166 tons of fresh weight of submerged vegetation, mainly Zostera, between September and March, incl. in the study years (Table
1). With a similar calculation the overall food consumption by the Coot was estimated to be between
Occurrence and numbers
Three species of plant feeders are of interest here
as they utilise submerged vegetation to a high degree, the Mute Swan Cygnus olor, the Whooper
Swan Cygnus cygnus and the Coot Fulica atra.
The Wigeon Anas penelope is another common
herbivor in the area, but it mostly feeds by graz-
Food requirements
15
Figure 2. Total numbers counted per ten-day periods of Mute Swan Cygnus olor, Whooper Swan Cygnus cygnus and Coot
Fulica atra in the study area during September–March 1995/96–1997/98. Among Whooper Swans, only those feeding on
aquatic areas are included.
Antal knölsvanar, sångsvanar och sothöns i undersökningsområdet i södra Öresund September–March 1995/96–1997/98.
Notera att endast sångsvanar som födosöker i havet är medräknade.
16
34 and 72 tons. Over the entire area, this compares
to 40 to 60 g/m2 fresh weight for the period September –March for the Coot and Swans in the area
if they can use all parts within “swan-depth”.
During the ice-period most areas with Ruppia
were covered by ice and not available to the feeding waterfowl. The calculated rate of food exploitation for the ice-free areas during the ice-period
in 1995/96 was high, 504 g/m2 , whereas the value
was lower for the shorter ice-period in 1996/97,
189 g/m2 (Table 2). To this should be added some
consumption by Coot.
Exploitation of food resources
In the autumn of 1995 the total standing crop of
Ruppia was measured in some areas in Lommabukten and around Klagshamn. For a depth of
0.4 m the standing crop varied between 62 and
152 g/m2 dry weight, whereas the standing crop at
the stations with a depth of 0.8 m varied between
44 and 82 g/m2 (VKI/Toxicon 1996a). Expressed
as wet-weight the values are about 6 times larger.
The standing crop of Zostera in the Öresund is also
high, maximum biomasses, which are reached in
August, amounting to 200–700 g DW/m2 in different areas (VKI/Toxicon 1996b) or 1200–4300 g
wet weight /m2. Part of the biomass is in the underground parts.
The standing crop of Ruppia varies markedly
over the season from nearly 200 g DW /m2 in some
stations in October it was about 70–100 g dry
weight in December and only a few gram in March.
If only the shoots are utilised the October values
are reduced to 75–80 g and the March values to 4
g. Zostera also shows a marked seasonal variation
in biomass from peak mean values of around 250
g DW/m2 in summer to a low of slightly more than
100 g DW/m2 for the above-ground parts in winter
(VKI/Toxicon 1996b, 1996c). This corresponds to
about 600 g wet weight/m2 for the above-ground
parts in December
In the autumn of 1996, the biomass of Zostera on
the Swedish side south of the link alignment was
between 65 and 165 g dry weight per m2, which is
between 390 and 990 g wet weight per m2 (SEMAC
1997, 1998). These values are however general
mean values and the biomass was lower in the more
shallow waters around 50 g dry weight. Moreover
the coverage of Zostera was around 70%, which
means available food resources of between 280 and
700 g wet weight per m2.
In general, the consumption rates of the plant
feeders were small compared to the available standing crop of Ruppia in the shallowest areas as is the
case for the parts of the Zostera meadows within
reach for the swans. The values presented in Table
1 indicate a consumption rate of about 10% less
17
Table 1. Calculation of food requirements for swans and Coot in the Foteviken–Lernacken area September–
March 1995/96–1997/98.
Beräkning av födobehovet för rastande och övervintrande svanar och sothöns mellan Foteviken och Lernacken
under september–mars 1995/97–1997/98.
Number of bird days
Antal fågeldagar
Cygnus olor knölsvan
Cygnus cygnus sångsvan
Total swans Summa svanar
Fulica atra sothöna
Total swans and Coot
Summa svanar och sothöna
Total food requirement (Ton wet weight)
Summa födobehov (ton våtvikt)
Swans svanar (3500 g/24h)
Fulica atra sothöna (300 g/24h)
Total Summa
Food requirements födobehov (g/m2)
Calculated for swan depth (2050 ha)
Beräknat för svandjup
than that of the available standing crop of food
plants. Similarly in an ice-free winter the available
food resources of Ruppia in these shallow waters
and Zostera in slightly deeper water would have
been more than sufficient for the wintering swans
and Coots in the area, only a small percentage of
the total standing crops being used.
During the ice-period in 1995/96 the total calculated food consumption per m2 was not much lower
than the normal standing crop values reported by
VKI/Toxicon (1996b, 1996c). Even if the biomass
values used for the Zostera are only general data
that varies much between different sites, it is clear
that the swans were close to the limit set by the
available food resources by the ice. It is however
probable that the effective feeding areas can have
been slightly larger than given in the calculations
here as the ice shifted position somewhat during
the winter, i.e. even if the total ice-free area was
similar. On the other hand some areas included in
the vegetated areas can have been without vegetation, which will not be taken into account when using overall mean values.
Discussion
According to the calculations presented here, the
staging and wintering Swans (mainly Mute Swans)
and Coots have rich food supplies in the Swedish
18
1995/96
1996/97
1997/98
322560
10752
333312
241017
218197
4620
222817
112847
230685
6776
237461
136409
921627
618422
527702
1166
72
1238
780
34
814
831
41
872
60
40
42
part of the Öresund with ample food resources of
Zostera and Ruppia within “swan-depth”. The overall food consumption of the swans and Coot during
September–March was calculated to be 10% or less
of the available standing crop of food plants. Even
if the study refers to the autumn and winter situation, the production of the Zostera vegetation has
not stopped by the beginning of September, so the
available food resources are actually higher than indicated by the comparison here. During the ice-free
periods of the cold winters and in ice-free winters
such as 1997/98 and 1998/99 the food resources of
Zostera and Ruppia were sufficient for much larger
numbers of swans (and Coot) than actually present
in the Öresund
Studies relating the food consumption of swans
and Coot to their food resources are few, but
Clausen & Krause-Jensen (1994) compared the
food consumption of herbivorous waterfowl and
Zostera production in a Danish fjord and calculated the mean grazing pressure on Zostera to be
12% of the production on an annual basis. Studies
on moulting Mute Swan in the Öresund were undertaken as a part of the Control Program for the
Fixed Link, also including comparisons between
swan numbers and available food resources. It was
generally concluded that the food resources were
plentiful for the moulting swans (cf. e.g. Kahlert
et al. 2000).
Table 2. Calculation of food requirements for swans and Coot in the Foteviken–Lernacken area during the ice
periods in 1995/96 and 1996/97. Note that the estimated food consumption here is 25% higher than in Table 1
(cf. Williams & Kendeigh 1982 as discussed in the text for colder pcriods).
Beräkning av födobehovet för övervintrande svanar och sothöns mellan Foteviken och Lernacken under isperioder 1995/97 och 1996/97. Observera att den beräknade födokosumtionen här är 25% högre än i Tabell 1 (jfr
Williams & Kendeigh 1982 för kallare perioder).
Ice-period Isperiod
Number of bird days
Antal fågeldagar
Cygnus olor knölsvan
Cygnus cygnus sångsvan
Total swans Summa svanar
Fulica atra sothöna
Total food requirements (ton wet weight)
Totalt födobehov (ton våtvikt)
Swans svanar (4375 g/24h)
Fulica atra sothöna (375 g/24h)
Total Summa
Available ice-free areas (mean in ha)
Tillgänglig isfri areal (medel i ha)
Swans svanar
Fulica atra sothöna
Food requirements (g/m2)
Födobehov
Swans svanar
Fulica atra sothöna
Total (g/ m2)
In the hard winters the situation was different as
the swans are restricted to the few ice-free areas
available and as they are moreover restricted to the
shallowest parts that are the first to freeze. During
the ice-period in the winter of 1995/96 the calculated food resources in the ice-free areas more or less
balanced the amount of food needed by the swans.
In this connection it must also be taken into consideration that the feeding waterfowl might reach a
limit where the food is getting more scarce and that
they accordingly cannot use all potentially available food resources.
It is well-known that Mute Swans and Coot suffer increased mortality due to food shortage in cold
winters (Andersen-Harild 1981, Cave & Wisser
1985, Nilsson 1991, 2002). In the Coot the indices from the Swedish waterfowl counts showed
a marked decrease after the hard winter of 1979,
which caused a high mortality among the Coots
(Nilsson 1991, unpubl.). The Swedish midwinter
indices do not show especially marked declines
after the hard winters for the Mute Swan, but the
1995/96
21 Dec–
31 Mar
1996/97
15 Dec–
10 Feb
163700
7700
171400
57000
60600
3700
64300
18600
750
21
771
282
8
290
150
490
180
570
500
4
504
188
2
190
September indices in 1979, 1982, 1985 and 1987,
i. e. years with hard ice-winters all show a decrease
in the index values.
Acknowledgements
The study was undertaken as a part of the Control
Programme for the Fixed Link between Sweden
and Denmark, on contract between Öresunds Konsortiet and Lund University. Most field work was
undertaken by Martin Green, Martin Granbom and
Lars Råberg.
References
Andersen-Harild, P. 1981. Population dynamics of Cygnus
olor in Denmark. Pp. 176–191 in Proceedings Second
International Swan Symposium, Sapporo, Japan, 21–22
February 1980 (G. V. T. Matthews & M. Smart, Eds.). International Waterfowl Research Bureaus, Slimbridge.
Borowiec, E. 1975. Food of the coot (Fulica atra) in different
Phenological periods. Pol. Arch. Hydrobiol. 22: 157–166.
Cavé, A. J. & Visser, J. 1985. Winter severity and breeding
19
bird numbers in a Coot population. Ardea 73: 129 – 138.
Clausen, P., Kahlert, J., Fox, A. D. & Andersen-Harild, P.
1995. Base-line Investigations of Moulting Mute Swans
on Saltholm, June–October 1994. NERI Report.
Clausen, P., Kahlert, J. Andersen-Harild, P. & Nilsson, L.
1996. Base-line Investigations of moulting Mute Swans
around Saltholm, 1993–1995: Results and Conclusions.
NERI Report.
Clausen, P. & Krause-Jensen, D. 1994. An annual budget of
eelgrass Zostera marina consumption by herbivorous waterfowl in a shallow Danish estuary. Pp. 100–111 in Vandfugles rolle som primaer-konsumenter i lavvandede fjordområder (Clausen, P. 1994. PhD afhandlig.) Danmarks
Miljöundersögelser/Aarhus Universitet. 126 s.
Hurter, H. 1972. Nahrung und Ernährungsweise des Blässhuhns Fulica atra am Sempachersee. Ornithologische Beobacheter 69: 125–149.
Hurter, H. 1979. Nahrungsökologie des Blässhuhns Fulica
atra an den Überwinterungsgewässern im nördlichen Alpenvorland. Ornithologische Beobachter 76: 257–288.
Kahlert, J., Clausen, P. & Nilsson, L. 2000. Monitoring of
moulting mute swans around Saltholm, 1999. NERI Report.
Mathiasson, S. 1973. A moulting population of nonbreeding Mute Swans with special reference to flightfeather
moult, feeding ecology and habitat selection. Wildfowl 24:
43–53.
Nilsson, L. 1975. Midwinter distribution and numbers of
Swedish Anatidae. Ornis Scandinavica 6: 83–107.
Nilsson, L. 1976. Monthly counts as a measure of population
changes in some species of Anatidae in south Sweden. Ornis Scandinavica 7: 193–205.
Nilsson, L. 1991. Distribution, population size and longterm changes in population size of wintering waterfowl in
Sweden. Ornis Svecia 1: 11–28. (In Swedish with English
summary).
Nilsson, L. 1996a. Resting and Wintering Waterfowl along
the Swedish coast of the Öresund, 1962– 1995. Report to
Öresundskonsortiet. Ecological Institute, University of
Lund.
Nilsson, L. 1996b. Monitoring of resting and wintering waterfowl along the Swedish coast of southern Öresund July
1995–June 1996 in relation to the Fixed-Link across the
Öresund. Report to Öresundskonsortiet. Ecological Institute, University of Lund.
Nilsson, L. 1998. Monitoring of resting and wintering waterfowl along the Swedish coast of southern Öresund July
1996–June 1997 in relation to the Fixed-Link across the
Öresund. Report to Öresundskonsortiet. Ecological Institute, University of Lund.
Nilsson, L. 1999a. Monitoring of resting and wintering waterfowl along the Swedish coast of southern Öresund July
1997 – March 1998 in relation to the Fixed-Link across
the Öresund. Report to Öresundskonsortiet. Ecological
Institute, University of Lund.
Nilsson, L. 1999a. Monitoring of Tufted Ducks Aythya fuligula and Mute Swans Cygnus olor along the Swedish coast
of southern Öresund July 1998 – March 1999 in relation
to the Fixed-Link across the Öresund. Report to Öresundskonsortiet. Ecological Institute, University of Lund.
Nilsson, L. 2001. Monitoring of Tufted Ducks Aythya fuligula
and Mute Swans Cygnus olor along the Swedish coast of
southern Öresund July 1999 – March 2000 in relation to
20
the Fixed-Link across the Öresund. Report to Öresundskonsortiet. Ecological Institute, University of Lund.
Nilsson, L.2002. Numbers of Mute Swans and Whooper
Swans in Sweden, 1967 – 2000. Waterbirds 25 (Special
Publication 1): 53 – 60.
SEMAC JV 1997. The Authorities’ Control and Monitoring
Programme for the Fixed Link Across Öresund. Benthic
Vegetation. Status Report 1996.
SEMAC JV. 1998. Myndighedernes kontrol- og overvågningsprogram for Öresundsforbindelsens kyst-til-kyst anlaeg. Bentisk Vegetation. Tillstandsrapport 1997.
Suter, W. 1982. Vergleichende Nahrungsökologie von überwinternden Tauchenten (Bucephala, Aythya) und Blässhuhn (Fulica atra) am Untersee-Ende/Hochrhein (Bodensee). Ornithologische Beobacheter. 79: 225–254.
Verhoeven, J.T.A. 1980. The ecology of Ruppia-dominated
communities in western Europe. III. Aspects of production, consumption and decomposition. Aquatic Botany 8:
209–253.
VKI/Toxicon. 1996a. Baseline Study of the Distribution and
Dynamics of Ruppia around Saltholm and along the Swedish Coast. Document No. 96/119/1E.
VKI/Toxicon. 1996b. Documentation of the Eelgrass Model
for Öresund. Document No. 95/134/2E.
VKI/Toxicon. 1996c. Dynamics of Eelgrass in Öresund and
Assessment of Impact of Shading on Eeelgrass Growth
at Different Depths and Times of Season. Document No
96/108/1E.
Williams, J. E. & Kendeigh, S. C. 1982. Energetics of the
Canada Goose. Journal of Wildlife Management. 46:
588–600.
Öresundskonsortiet 1995. The Öresund Link. Supplementary
Assessment of the Impacts on the Marine Environment of
the Öresund Link.
Öresundskonsortiet 1998. Assessment of the Impacts on the
Marine Environment of the Öresund Link.
Sammanfattning
Södra Öresund är sedan gammalt känt som ett
viktigt rast och vinterområde för ett flertal olika
sjöfågelarter (Nilsson 1991). Många delområden uppfyller också kriterierna för internationellt
skyddsvärda våtmarksområden. Beroende på områdets betydelse för fågelfaunan kom studier av de
rastande och övervintrande sjöfåglarna att innefattas i kontrollprogrammet för den fasta förbindelsen
över Öresund, vilken byggdes under den senare delen av 1990-talet och stod färdig sommaren 2000.
Förbindelsen som är 16 km lång består av en kombinerad järnväg/motorväg från Lernacken på den
svenska sidan till Kastrup på den danska sidan.
Innefattande 1092 m högbro, 6700 m anslutningsbroar, 3500 m sänktunnel sam en konstgjord ö.
Villkoren för Öresundsförbindelsen stipulerade
bl.a. att den inte får påverka strömmarna ut och in
i Östersjön. För att uppfylla detta krav genomfördes en del kompenserande muddringar i anslutning
till bron. Felaktigt genomförda muddringar skulle
kunna medföra ökat sedimentspill i Öresund och
därmed en negativ påverkan på områdets undervattensfauna och flora. Omfattande studier av bottenfaunan oh floran (främst Zostera och Ruppia) kom
därför att inkluderas i kontrollprogrammet och gav
därmed förutsättningar för jämförelser mellan svanarnas och sothönsens födokrav och tillgången på
föda i området.
I den här uppsatsen jämförs svanarnas och sothönsens förekomst i området i relation till de
tillgängliga födoresurserna, medan inventeringarna kommer att presenteras mer i detalj i ett annat sammanhang (L. Nilsson & M. Green in prep.),
för detaljer från fågelinventeringarna inom kontrollprogrammet hänvisas till de tekniska rapporterna (Nilsson 1996a, 1996b, 1998, 1999a, 1999b,
2001).
Undersökningsområde
Kontrollprogrammet omfattade på den svenska sidan kusten mellan Falsterbo och Barsebäck, men
de här behandlade studierna genomfördes i området mellan brofästet vid Lernacken och Falsterbo
kanal (Figur 1). Området kännetecknas av stora
arealer grunt eller mycket grunt vatten. På de inre
lerbottnarna finns en rik vegetation av Ruppia,
medan omfattande Zostera-ängar återfinns på sandbottnarna längre ut V(KI/Toxicon 1999a, 1999b,
1999c, SEMAC 1997, 1998).
Material och Metoder
Fåglarnas utnyttjande av området har beräknats
som ”fågel-dagar”. Under 1995/96 och 1996/97 inventerades området mellan Barsebäck och Falsterbo, medan inventeringarna 1997/98 begränsades
till området mellan Lernacken och Falsterbo kanal.
Hela området inventerades en gång per vecka.
Fåglarnas födobehov baseras på uppgifter hämtade från litteraturen (Clausen et al. 1995, 1996, Mathiasson 1973). I mina beräkningar har jag använt
3,5 kg färskvikt av Zostera per dygn som ett mått
på svanarnas födobehov. För kalla perioder fann
William & Kendeigh (1982) att energiåtgången för
gäss och andra andfåglar var ca 25–30% högre. Jag
har i beräkningarna använt ett motsvarande högre
värde för isperioderna. Sothönans energibehov har
bl.a. studerats av Hurter (1972, 1979) samt Verhoeven (1980). Baserat på dessa studier har jag i mina
beräkningar utgått från 305 g färskvikt per dygn
för sothönan.
Resultat
De viktigaste växtätande arterna i området var
knölsvan, sångsvan och sothöna. Bläsanden förekommer också allmänt i området, men eftersom
den huvudsakligen betar på strandängarna har jag
inte tagit med den här även om den ibland kan furagera på Zostera som rivits loss av svanarna.
Antalet svanar och sothöns i området framgår av
Figur 2. 1995/96 sågs som mest mellan 2000 och
2500 knölsvanar i området, medan det högsta antalet de båda andra undersökningsåren låg mellan
1500 och 2000. Antalet sångsvanar var väsentligt
lägre, men jag har här endast räknat med de sångsvanar som söker föda i vattnet. För sothönsens del
noterades som mest ca 2000 individ i undersökningsområdet.
Totalt beräknades svanarna i undersökningsområdet konsumera mellan 780 och 1166 ton färskvikt
av undervattensvegetation, huvudsakligen Zostera
mellan september och mars. Till detta skall läggas
mellan 34 och 72 ton för sothönsen. Detta motsvarar totalt mellan 40 och 60 g/m2 (Tabell 1). Under
isperioderna begränsades särskilt svanarnas födosöksareal högst väsentligt (Tabell 2) och under
särskilt isperioden 1995/96 var födouttaget ca 500
g/m2.
Jämfört med mängden tillgänglig föda beräknades att svanarna och sothönsen under isfria förhållanden utnyttjade ca 10% eller mindre av den tillgängliga biomassan. Uttaget av föda var egentligen
lägre eftersom viss produktion fortfarande sker
under hösten. Under isperioderna närmade sig det
beräknade födouttaget mängden tillgänglig föda.
Diskussion
Studierna visar klart att födotillgången för svanar och sothöns i undersökningsområdet i södra
Öresund är tillräckliga för betydligt större mängder fåglar än vad som nu utnyttjar området. Totalt
beräknades de utnyttja 10% eller mindre av den
tillgängliga biomassan. Clausen & Krause-Jensen
(1994) fann från en dansk fjord att de växtätande
fåglarna (främst knölsvan) konsumerade ca 12% av
produktionen.
Under isperioden 1995/96 var dock födotillgången knapp. Både sothöna (Cavé & Visser 1985) och
knölsvan (Andersen-Harild 1981) visar under sådana förhållanden förhöjd dödlighet, vilket också
återspeglas i de svenska andfågelindexen (Nilsson
1991, 2002).
21